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EC number: 947-320-5 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 26 July 2019 to 14 August 2019
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on test conditions:
- The Test Solutions were kept between 49.8 – 50.3 °C.
HYDROLYSIS – TIER 1
5 – 5 tubes with test media (at all pH levels) were spiked with the spiking solution. All tubes were sampled after dissolution of the test material (Day-0) and the samples were processed as described above. 1 – 1 control tubes at all pH levels were also prepared (test buffer without spiking) to check the potential interfering components from the buffer. The test solutions and control test buffer were incubated at 50 °C for 5 days. After the incubation period all tubes were sampled again both control tubes were sampled, processed and measured.
CALCULATIONS
To determine the test item concentration in the saturated solutions the following calculations were applied:
The concentration of the test solution was calculated using the following equation:
CTestSol = ((Peak Area Average – Intercept) / Slope) x AnDil
Where:
cTestSol is the test item concentration in the test solution (mg/L)
Intercept is the intercept of the calibration curve
Slope is the slope of the calibration curve
AnDil. is the dilution of the analytical sample after the enrichment
The stability was determined:
Stability % = (ci / C0) x 100 %
Where:
c0 and ci are the test item concentrations measured on the initial and the end point of the experiment (mg/L) - Duration:
- 5 d
- pH:
- 4
- Temp.:
- 50 °C
- Initial conc. measured:
- ca. 1 000 mg/L
- Duration:
- 5 d
- pH:
- 7
- Temp.:
- 50 °C
- Initial conc. measured:
- ca. 1 000 mg/L
- Duration:
- 5 d
- pH:
- 9
- Temp.:
- 50 °C
- Initial conc. measured:
- ca. 1 000 mg/L
- Number of replicates:
- Six replicates per pH.
- Positive controls:
- not specified
- Negative controls:
- not specified
- Preliminary study:
- The test solutions were kept between 49.8 – 50.3 °C.
At pH 4 the mean stability from 6 replicates was 101.0 % (1.3 % RSD).
At pH 7 the mean stability from 6 replicates was 100.8 % (1.6 % RSD).
At pH 9 the mean stability from 6 replicates was 98.6 % (1.0 % RSD).
The test material is hydrolytically stable at 50 °C. - Transformation products:
- not measured
- % Recovery:
- 100
- St. dev.:
- 1.3
- pH:
- 4
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- hydrolytically stable based on preliminary test
- % Recovery:
- 100
- St. dev.:
- 1.6
- pH:
- 7
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- hydrolytically stable based on preliminary test
- % Recovery:
- 98.6
- St. dev.:
- 1
- pH:
- 9
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- hydrolytically stable based on preliminary test
- Remarks on result:
- hydrolytically stable based on preliminary test
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Under the conditions of the study the test material is hydrolytically stable in the range pH 4 – 9.
- Executive summary:
The hydrolytic properties of the test material were assessed according to OECD Test Guideline 111 and in compliance with GLP using an HPLC method.
Six replicates were conducted at pH 4, pH 7 and pH 9.
Tubes with test media (at all pH levels) were spiked with the spiking solution. All tubes were sampled after dissolution of the test item (Day-0) and the samples were processed as described above. Control tubes at all pH levels were also prepared (test buffer without spiking) to check the potential interfering components from the buffer.
The test solutions and control test buffer were incubated at 50 °C for 5 days. After the incubation period all tubes were sampled again both control tubes were sampled, processed and measured.
Under the conditions of the study the test material is hydrolytically stable in the range pH 4 – 9.
Reference
Summary of the Results
Sample |
pH |
CDay-0 (mg/L) |
CDay-5 (mg/L) |
Stab (%) |
Mean Stab (%) |
RSD% |
ST-202-HYD1-TS-410 |
4 |
0.00 |
< LOQ |
N/A |
N/A |
N/A |
ST-202-HYD1-TS-411 |
4 |
26.43 |
26.71 |
101.1 |
101.0 |
1.3 |
ST-202-HYD1-TS-412 |
4 |
26.27 |
26.57 |
101.1 |
||
ST-202-HYD1-TS-413 |
4 |
26.19 |
25.86 |
98.7 |
||
ST-202-HYD1-TS-414 |
4 |
25.97 |
26.49 |
102.0 |
||
ST-202-HYD1-TS-415 |
4 |
26.43 |
26.95 |
102.0 |
||
ST-202-HYD1-TS-710 |
7 |
0.00 |
< LOQ |
N/A |
N/A |
N/A |
ST-202-HYD1-TS-711 |
7 |
26.06 |
26.27 |
100.8 |
100.8 |
1.6 |
ST-202-HYD1-TS-712 |
7 |
25.89 |
26.52 |
102.5 |
||
ST-202-HYD1-TS-713 |
7 |
26.55 |
26.30 |
99.1 |
||
ST-202-HYD1-TS-714 |
7 |
27.02 |
26.82 |
99.2 |
||
ST-202-HYD1-TS-715 |
7 |
26.21 |
26.79 |
102.2 |
||
ST-202-HYD1-TS-910 |
9 |
0.00 |
< LOQ |
N/A |
N/A |
N/A |
ST-202-HYD1-TS-911 |
9 |
25.88 |
25.09 |
96.9 |
98.6 |
1.0 |
ST-202-HYD1-TS-912 |
9 |
27.07 |
26.80 |
99.0 |
||
ST-202-HYD1-TS-913 |
9 |
26.11 |
25.88 |
99.1 |
||
ST-202-HYD1-TS-914 |
9 |
26.66 |
26.39 |
99.0 |
||
ST-202-HYD1-TS-915 |
9 |
26.60 |
26.31 |
98.9 |
Description of key information
Under the conditions of the study the test material is hydrolytically stable in the range pH 4 – 9.
Key value for chemical safety assessment
Additional information
The hydrolytic properties of the test material were assessed according to OECD Test Guideline 111 and in compliance with GLP using an HPLC method.
Six replicates were conducted at pH 4, pH 7 and pH 9.
Tubes with test media (at all pH levels) were spiked with the spiking solution. All tubes were sampled after dissolution of the test item (Day-0) and the samples were processed as described above. Control tubes at all pH levels were also prepared (test buffer without spiking) to check the potential interfering components from the buffer.
The test solutions and control test buffer were incubated at 50 °C for 5 days. After the incubation period all tubes were sampled again both control tubes were sampled, processed and measured.
Under the conditions of the study the test material is hydrolytically stable in the range pH 4 – 9.
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